TW202021901A - Method for the recycling or disposal of halocarbons - Google Patents

Method for the recycling or disposal of halocarbons Download PDF

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TW202021901A
TW202021901A TW108144446A TW108144446A TW202021901A TW 202021901 A TW202021901 A TW 202021901A TW 108144446 A TW108144446 A TW 108144446A TW 108144446 A TW108144446 A TW 108144446A TW 202021901 A TW202021901 A TW 202021901A
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halocarbon
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sulfuric acid
halocarbon compound
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TWI737064B (en
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提摩 奧特
尤羅夏 克里斯汀 迪亞斯
麥堤亞斯 佛格特
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德商格里洛工廠股份有限公司
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    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C303/00Preparation of esters or amides of sulfuric acids; Preparation of sulfonic acids or of their esters, halides, anhydrides or amides
    • C07C303/02Preparation of esters or amides of sulfuric acids; Preparation of sulfonic acids or of their esters, halides, anhydrides or amides of sulfonic acids or halides thereof
    • C07C303/04Preparation of esters or amides of sulfuric acids; Preparation of sulfonic acids or of their esters, halides, anhydrides or amides of sulfonic acids or halides thereof by substitution of hydrogen atoms by sulfo or halosulfonyl groups
    • C07C303/06Preparation of esters or amides of sulfuric acids; Preparation of sulfonic acids or of their esters, halides, anhydrides or amides of sulfonic acids or halides thereof by substitution of hydrogen atoms by sulfo or halosulfonyl groups by reaction with sulfuric acid or sulfur trioxide
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/30Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]

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Abstract

The present invention relates to a method for recycling and/or disposal of halocarbons, particularly fluorinated alkanes, such as trifluoromethane, by reacting said halocarbons with sulfur trioxide, particularly to form halide sulfonic acids and sulfur dioxide。

Description

用於鹵碳化合物的回收或處置的方法Method for recovery or disposal of halocarbon compounds

本發明係關於鹵碳化合物(特別是氟代烷,諸如三氟甲烷)的回收及/或處置的方法,藉由鹵碳化合物與三氧化硫反應,特別是形成氫鹵化物(hydrogen halide)、二氧化碳及二氧化硫。本發明意義中之回收/處置表示將鹵碳化合物轉換成有用的物質。The present invention relates to a method for the recovery and/or disposal of halocarbon compounds (especially fluoroalkanes, such as trifluoromethane). By reacting halocarbon compounds with sulfur trioxide, especially the formation of hydrogen halide, Carbon dioxide and sulfur dioxide. Recycling/disposal in the meaning of the present invention means the conversion of halocarbon compounds into useful substances.

鹵碳化合物係指烴中至少一個氫原子被鹵素取代後之化合物。烴為可任何類型的烴,即烷烴、烯烴、及炔烴(alkine),其可為直鏈的、支鏈的、或環狀的,經取代或未經取代的。鹵代烷為鹵碳化合物的一部分,亦稱為鹵烷(halogenalkane)或烷基鹵化物,其結構係透過用鹵素原子取代烷烴中之一或多個氫原子所衍生之一類化合物。鹵烷係廣泛地用作阻燃劑、滅火劑、冷凍劑、推進劑、溶劑及藥物。Halocarbon compounds refer to compounds in which at least one hydrogen atom in a hydrocarbon is replaced by halogen. Hydrocarbons can be any type of hydrocarbons, namely alkanes, alkenes, and alkynes, which can be linear, branched, or cyclic, substituted or unsubstituted. Halogenated alkanes are part of halocarbon compounds, also known as halogenalkanes or alkyl halides. Its structure is a type of compound derived by substituting halogen atoms for one or more hydrogen atoms in alkanes. Haloalkanes are widely used as flame retardants, fire extinguishing agents, refrigerants, propellants, solvents and drugs.

氫氯氟烷(hydrochlorofluoroalkane)因造成臭氧層破壞而在上一世紀(蒙特婁議定書,1987年)於國際上被禁用,此誘發在其他應用上發展新穎的氟烷以用作冷凍劑及氣體推進劑之替代選項。氟烷之獨特的性質,諸如高穩定性及惰性,因而係氫氯氟碳之理想的替代物。然而,後續研發顯示氟烷為潛在的溫室氣體。例如,小小的氟仿(CF3 H)之溫室效應的潛能係與14,800個CO2 分子相同。Hydrochlorofluoroalkane (hydrochlorofluoroalkane) was banned internationally in the last century (Montreal Protocol, 1987) due to the destruction of the ozone layer, which induced the development of novel halothanes for other applications as refrigerants and gas propellants The alternative option. The unique properties of halothane, such as high stability and inertness, make it an ideal substitute for hydrochlorofluorocarbon. However, subsequent research and development show that halothane is a potential greenhouse gas. For example, the greenhouse effect of a small fluoroform (CF 3 H) has the same potential as 14,800 CO 2 molecules.

國際上成功地逐漸禁止氟烷的使用,且與直至2045年相較於基準量欲削減85%(針對蒙特婁議定書於2016年所通過之吉佳利(Kigali)修正案)。具有較低全球暖化潛勢值(global warming potential)且對於臭氧層係無害之替代氣體現正在研究中,且很多成功產品已在市場上使用。The internationally succeeded in gradually banning the use of halothane, and compared to the baseline by 2045, it will be reduced by 85% (the Kigali amendment passed in 2016 for the Montreal Protocol). Alternative gases with low global warming potential and harmless to the ozone layer are currently being studied, and many successful products have been used in the market.

然而,多種大規模產業製程會產生為副產物之氟烷。例如,作為冷凍劑之氯二氟甲烷(HCF2 Cl)之合成、用於發泡材料之摻合組分及聚四氟乙烯(鐵氟龍(Teflon)),會產生大量CF3 H,而為符合現今法規導致進行儲存或回收之額外成本。氟烷的儲存,經濟上並非可行的,因而回收變成唯一的合理選項。However, many large-scale industrial processes produce halothane as a by-product. For example, the synthesis of chlorodifluoromethane (HCF 2 Cl) as a refrigerant, the blending component for foaming materials, and polytetrafluoroethylene (Teflon), will produce a large amount of CF 3 H, and In order to comply with current regulations, additional costs for storage or recycling are caused. The storage of halothane is not economically feasible, so recycling becomes the only reasonable option.

現今之一些方法(A. McCulloch發表之標題「焚化HFC-23廢棄流份以減少來自HFCFC-22之排放:科學、技術及經濟方面之評論(Incineration of HFC-23 waste streams for abatement of emissions from HFCFC-22 production: A review of scientific, technical and economic aspects)」, 布里斯托大學(University of Bristol),2005年)係使用H2 及CO2 在300至900o C進行氟烷之熱催化分解,產生CO及HF。高溫操作及HF的產生係這些方法被廣泛應用之主要限制。對於工業規模製造所衍生之鹵碳化合物(特別是氟烷)回收係需要有新穎的方法。Some current methods (A. McCulloch published the title "Incineration of HFC-23 waste streams to reduce emissions from HFCFC-22: Science, Technology, and Economic Review (Incineration of HFC-23 waste streams for abatement of emissions from HFCFC) -22 production: A review of scientific, technical and economic aspects)”, University of Bristol (University of Bristol, 2005) uses H 2 and CO 2 to perform thermal catalytic decomposition of halothane at 300 to 900 o C. Produce CO and HF. High temperature operation and HF generation are the main limitations of these methods being widely used. For the recovery system of halocarbon compounds (especially halothane) derived from industrial-scale manufacturing, novel methods are needed.

本發明目的因而在於提供一種用於鹵碳化合物(特別是氟烷)的回收或處置之新穎方法,以及將其轉換成對於臭氧層無害且不呈現相當的(considerable) 全球暖化潛勢值之物質。特別地,本發明目的係提供一種將鹵碳化合物轉換成有用物質之有效方法。The object of the present invention is therefore to provide a novel method for the recovery or disposal of halocarbon compounds (especially halothanes), and to convert them into substances that are harmless to the ozone layer and do not exhibit equivalent global warming potential. . In particular, the object of the present invention is to provide an effective method for converting halocarbon compounds into useful substances.

驚訝地發現到,鹵碳化合物與SO3 反應形成帶有鹵碳化合物之鹵素的磺酸(sulfonic acid)。在第一實施態樣,本發明目的因而藉由一種用於鹵碳化合物之轉換的方法而達成,其中,鹵碳化合物與SO3 反應,較佳地,鹵碳化合物與發煙硫酸(oleum)反應,其中,發煙硫酸(oleum)為發煙的硫酸(fuming sulfuric acid)。其係指SO3 溶於H2 SO4 的溶液。若儲存,SO3 與H2 SO4 反應形成二硫酸。若二硫酸作為反應之一組分,其通常再分解成SO3 及H2 SO4 ,所以SO3 通常係參加反應的反應夥伴。Surprisingly, it was found that the halocarbon compound reacts with SO 3 to form a sulfonic acid with the halogen of the halocarbon compound. In the first embodiment, the object of the present invention is thus achieved by a method for conversion of halocarbon compounds, in which halocarbon compounds react with SO 3 , preferably halocarbon compounds and oleum In the reaction, oleum is fuming sulfuric acid. It refers to a solution of SO 3 dissolved in H 2 SO 4 . If stored, SO 3 reacts with H 2 SO 4 to form disulfuric acid. If disulfuric acid is used as a component of the reaction, it is usually decomposed into SO 3 and H 2 SO 4 , so SO 3 is usually the reaction partner participating in the reaction.

在本發明的意義中,鹵碳化合物係為烴中至少一個氫原子被鹵素取代後之化合物。烴為可任何類型的烴,即烷烴、烯烴、及炔烴,其可為直鏈的、支鏈的、或環狀的,經取代或未經取代的。且在本發明的範疇內,若烴為芳基化合物,諸如苯酚、萘酚、苯(benzol)等,經取代在此上下文中係被理解為鹵碳化合物中之氫原子或C或CH基團或CH2 基團或CH3 基團被取代基取代。此取代基可為–COOH、C(O)、N、P、S、O、C(O)O,其中,若需要,自由價(free valences)被氫飽和。In the meaning of the present invention, a halocarbon compound is a compound in which at least one hydrogen atom in a hydrocarbon is replaced by a halogen. Hydrocarbons can be any type of hydrocarbons, namely alkanes, alkenes, and alkynes, which can be linear, branched, or cyclic, substituted or unsubstituted. And within the scope of the present invention, if the hydrocarbon is an aryl compound, such as phenol, naphthol, benzol, etc., substitution in this context is understood as a hydrogen atom or a C or CH group in a halogenated carbon compound Or the CH 2 group or the CH 3 group is substituted by a substituent. This substituent can be -COOH, C(O), N, P, S, O, C(O)O, where, if necessary, free valences are saturated with hydrogen.

若在下文中提及鹵碳化合物與SO3 反應,應被理解為該反應係與純的SO3 或與發煙硫酸反應。較佳地,發煙硫酸係存在以使鹵碳化合物與SO3 反應進行。在本發明的範疇內,硫酸或水係於第一步驟中提供而隨後加入之SO3 ,因此發煙硫酸在反應混合物中原處形成。當然,亦可先提供SO3 ,及隨後加入水或硫酸,同樣亦會形成發煙硫酸。If the reaction of halocarbon compounds with SO 3 is mentioned in the following, it should be understood that the reaction is with pure SO 3 or with fuming sulfuric acid. Preferably, the fuming sulfuric acid is present to allow the halocarbon compound to react with SO 3 . Within the scope of the present invention, sulfuric acid or water is provided in the first step and then added SO 3 , so that fuming sulfuric acid is formed in situ in the reaction mixture. Of course, it is also possible to provide SO 3 first, and then add water or sulfuric acid, which will also form oleum.

SO3 可以大範圍之濃度溶於H2 SO4 。因此,在本應用的意義中,發煙硫酸包括1重量%至100重量%的SO3 ,在發煙硫酸中SO3 含量較佳係10%至95%,特別地15%至90%,較佳地20%至88%,更佳地25%至85%或30%至80%,特別地35%至75%或40%至70%。較佳地,SO3 含量係65重量%或更低,特別地60重量%或更低。在鹵碳化合物與發煙硫酸間之安全反應進行下,SO3 含量越高,處理發煙硫酸的風險及控制反應條件的風險越高。若SO3 濃度低,特別是低於10%,反應時間相當長。因此,特別是在SO3 於發煙硫酸中之濃度為25重量%至70重量,較佳30重量%至65重量,有效反應可進行。SO 3 can be dissolved in H 2 SO 4 in a wide range of concentrations. Therefore, in the meaning of this application, oleum includes 1% to 100% by weight of SO 3. The content of SO 3 in oleum is preferably 10% to 95%, especially 15% to 90%, which is more Preferably it is 20% to 88%, more preferably 25% to 85% or 30% to 80%, particularly 35% to 75% or 40% to 70%. Preferably, the SO 3 content is 65% by weight or less, especially 60% by weight or less. Under the safe reaction between halocarbon compounds and fuming sulfuric acid, the higher the SO 3 content, the higher the risk of treating fuming sulfuric acid and controlling the reaction conditions. If the SO 3 concentration is low, especially below 10%, the reaction time is quite long. Therefore, especially when the concentration of SO 3 in fuming sulfuric acid is 25% to 70% by weight, preferably 30% to 65% by weight, effective reaction can proceed.

在本申請案中,若沒有另外明確說明,%係永遠指重量%。In this application, if not explicitly stated otherwise,% always refers to% by weight.

特定地,鹵碳化合物係與三氧化硫反應形成對應的磺酸。對應的磺酸在此上下文中係指包括與所使用之鹵碳化合物相同鹵素(F、Cl、Br、I、As)的磺酸。在其中鹵碳化合物包括多於一種類型之鹵素(F、Cl、Br、I、As),則形成多種類型之磺酸。Specifically, halocarbon compounds react with sulfur trioxide to form corresponding sulfonic acids. The corresponding sulfonic acid in this context refers to a sulfonic acid that includes the same halogen (F, Cl, Br, I, As) as the halocarbon compound used. Where the halocarbon compound includes more than one type of halogen (F, Cl, Br, I, As), multiple types of sulfonic acid are formed.

例如,若HCF3 與發煙硫酸反應,反應產物為FSO3 H、SO2 及CO2 。SO2 在發煙硫酸中具有高溶解度。其可再氧化成SO3 及後續用於另一鹵碳化合物的回收。FSO3 H可作為工業上化學物質,CO2 相較於進行轉換之鹵碳化合物係具有顯著較小的全球暖化潛勢值。For example, if HCF 3 reacts with fuming sulfuric acid, the reaction products are FSO 3 H, SO 2 and CO 2 . SO 2 has high solubility in fuming sulfuric acid. It can be re-oxidized to SO 3 and subsequently used in the recovery of another halocarbon compound. FSO 3 H can be used as an industrial chemical substance, and CO 2 has a significantly smaller global warming potential value than the halocarbon compounds undergoing conversion.

或者,若H2 CF2 與發煙硫酸反應,形成FSO3 H: CH2 F2 + 2SO3 + H2 SO4 à CH2 (SO4 H)2 + 3FSO3 H; CH2 F2 與發煙硫酸反應產生氟磺酸及伸甲基二(硫酸酯)(methylene di(sulfate),MDS)。與使用CHF3 之類似反應之不同處在於碳沒進行氧化反應。因此,CO2 及SO2 的形成都沒有觀察到。Or, if H 2 CF 2 reacts with fuming sulfuric acid to form FSO 3 H: CH 2 F 2 + 2SO 3 + H 2 SO 4 à CH 2 (SO 4 H) 2 + 3FSO 3 H; CH 2 F 2 and FA The oleum reaction produces fluorosulfonic acid and methylene di(sulfate) (MDS). The difference from a similar reaction using CHF 3 is that the carbon does not undergo an oxidation reaction. Therefore, neither the formation of CO 2 nor SO 2 was observed.

MDS基本上係甲醛衍生物,水解時,甲醛及硫酸被釋放。MDS以其縮合之二聚物形式適合作為殺生物劑、用於人造板(抗菌及防腐多功用無醛秸稈人造板)之緩釋性防霉劑、在電池應用中作為電解質。MDS is basically a formaldehyde derivative. When hydrolyzed, formaldehyde and sulfuric acid are released. MDS in its condensed dimer form is suitable as a biocide, a slow-release antifungal agent for artificial panels (antibacterial and anti-corrosion multifunctional non-formaldehyde straw artificial panels), and as an electrolyte in battery applications.

不受限於理論,下列反應通常會發生(其中,X為鹵素): CH2 X2 + 2SO3 + H2 SO4 à CH2 (SO3 H)2 + 2XSO3 H,X=F CH2 X2 + 2SO3 à CH2 (SO3 X)2 ,X=Cl、Br、I CH2 X2 過量的之反應:CH2 (SO3 X)2 + CH2 X2 à 2  XCH2 (SO3 X)Without being bound by theory, the following reactions usually occur (where X is a halogen): CH 2 X 2 + 2SO 3 + H 2 SO 4 à CH 2 (SO 3 H) 2 + 2XSO 3 H, X=F CH 2 X 2 + 2SO 3 à CH 2 (SO 3 X) 2 , X=Cl, Br, I CH 2 X 2 Excessive reaction: CH 2 (SO 3 X) 2 + CH 2 X 2 à 2 XCH 2 (SO 3 X)

在各自反應條件下會進行下列水解反應: CH2 (SO3 X)2 + 2H2 O à CH2 (SO4 H)2 + 2HX 2HX + SO3 à 2XSO3 H CH2 (SO3 X)2 + H2 O à (XSO3 )-CH2 -(SO4 H) + HX HX + SO3 à XSO3 HThe following hydrolysis reactions will proceed under respective reaction conditions: CH 2 (SO 3 X) 2 + 2H 2 O à CH 2 (SO 4 H) 2 + 2HX 2HX + SO 3 à 2XSO 3 H CH 2 (SO 3 X) 2 + H 2 O à (XSO 3 )-CH 2 -(SO 4 H) + HX HX + SO 3 à XSO 3 H

假設的反應說明於下:

Figure 02_image001
The hypothetical response is illustrated below:
Figure 02_image001

並非僅包含一個碳原子的烷可轉換成對應磺酸,具有更高碳數的烷也可轉換成對應磺酸。可被發煙硫酸轉換之鹵碳化合物需要至少一個結構元素,其可進行親核攻擊、親電子攻擊或自由基攻擊。此例如雙鍵或三鍵或C-H、C-Cl、-C-Br、CI、C-COOH、C-SO2 H、或C-SO3 H、C-NH2 、C-OH、C=O、CN基團。Not only an alkane containing one carbon atom can be converted into the corresponding sulfonic acid, an alkane with a higher carbon number can also be converted into the corresponding sulfonic acid. The halocarbon compound that can be converted by fuming sulfuric acid requires at least one structural element, which can perform nucleophilic attack, electrophilic attack, or free radical attack. Such as double bond or triple bond or CH, C-Cl, -C-Br, CI, C-COOH, C-SO 2 H, or C-SO 3 H, C-NH 2 , C-OH, C=O , CN group.

較佳的情況為,鹵碳化合物包括二、三、或四個碳原子,反應混合物不僅包括鹵碳化合物及發煙硫酸,亦包括氧化劑。該氧化劑需以相對於存在反應混合物中鹵碳化合物含量之化學計量加入。適當氧化劑例如過氧化物、H2 O2 、K2 S2 O8 及其他穩定的化合物。氧化劑會在下文更詳細地討論。Preferably, the halocarbon compound includes two, three, or four carbon atoms, and the reaction mixture includes not only the halocarbon compound and fuming sulfuric acid, but also an oxidant. The oxidant needs to be added in a stoichiometric amount relative to the content of halocarbon compounds present in the reaction mixture. Suitable oxidizing agents such as peroxides, H 2 O 2 , K 2 S 2 O 8 and other stable compounds. The oxidizer will be discussed in more detail below.

可根據本發明方法進行回收/處置之鹵碳化合物例如F3 C-CHF=CH2 (1234yf),其為用於空氣條件(尤其是汽車及其他交通工具內的空氣條件)之冷媒。同樣地,該化合物、發煙硫酸與氧化劑反應產生SO2 及FSO3 H。此外,長鏈鹵碳化合物,諸如具有-COOH或-SO3 H端基之鹵代表面活性劑,藉由加入發煙硫酸,可被轉換成XSO3 H(X為鹵素)及SO2 。直鏈及環狀鹵碳化合物均可使用本發明方法進行轉換。Halocarbon compounds that can be recovered/disposed according to the method of the present invention are, for example, F 3 C-CHF=CH 2 (1234yf), which is a refrigerant used in air conditions (especially air conditions in automobiles and other vehicles). Similarly, the compound, fuming sulfuric acid and oxidant react to produce SO 2 and FSO 3 H. In addition, long-chain halocarbon compounds, such as halogens with -COOH or -SO 3 H end groups, can be converted into XSO 3 H (X is halogen) and SO 2 by adding fuming sulfuric acid. Both linear and cyclic halocarbon compounds can be converted using the method of the present invention.

本發明方法提供用於鹵碳化合物的回收或處置之簡易且便宜的方法以及鹵碳化合物被轉換成有用的物質,特別是在工業製程中所產生為副產物之鹵碳化合物,諸如鐵氟龍(Teflon)。本發明方法可直接在產生鹵碳化合物之原址上以小規模設備進行。The method of the present invention provides a simple and inexpensive method for the recovery or disposal of halocarbon compounds and the conversion of halocarbon compounds into useful substances, especially halocarbon compounds produced as by-products in industrial processes, such as Teflon (Teflon). The method of the present invention can be directly carried out with small-scale equipment on the original site where halocarbon compounds are produced.

本發明使用三氧化硫進行鹵碳化合物之轉換方法可在不使用任何金屬催化劑下進行。較佳地,本發明方法係在無金屬催化劑下進行。The method for converting halocarbon compounds using sulfur trioxide in the present invention can be carried out without using any metal catalyst. Preferably, the method of the present invention is carried out without a metal catalyst.

本發明方法可使用在原位上形成之過氧化物或稀的過氧化物鹽類(諸如K2 S2 O8 )作為催化劑或於化學計量之用量下進行。原則上,任何在室溫下為穩定之過氧化物可用做催化劑。特別地,可使用含氧酸之過氧酸或其鹽類。更明確地,可使用硫之含氧酸之過氧酸或其鹽類。或者,可使用過氧化氫與含氧酸之混合物。明確的例子包括:H2 S2 O8 、K2 S2 O8 、Na2 S2 O8 、H2 SO5 、KHSO5 、NaHSO5 等。這些催化劑/氧化劑可使SO2 再氧化成SO3 。因此, SO3 的用量可減少。此效果與鹵碳化合物僅包括一個碳原子係特別有關聯的。The method of the present invention can use peroxides or dilute peroxide salts (such as K 2 S 2 O 8 ) formed in situ as a catalyst or be carried out in a stoichiometric amount. In principle, any peroxide that is stable at room temperature can be used as a catalyst. In particular, peroxyacids containing oxoacids or salts thereof can be used. More specifically, peroxyacids or their salts, which are oxoacids of sulfur, can be used. Alternatively, a mixture of hydrogen peroxide and oxyacid can be used. Specific examples include: H 2 S 2 O 8 , K 2 S 2 O 8 , Na 2 S 2 O 8 , H 2 SO 5 , KHSO 5 , NaHSO 5 and so on. These catalysts/oxidants can re-oxidize SO 2 to SO 3 . Therefore, the amount of SO 3 can be reduced. This effect is particularly related to the halocarbon compound including only one carbon atom system.

鹵碳化合物中之碳數為>1,即,2、3、4、5、6、7、8、9、10或更高時,氧化劑以化學計量加入似乎係需要的。此處,氧化劑活化鹵碳化合物,使之趨向降解。藉助於氧化催化劑/氧化用劑(oxidating agent)/氧化劑(oxidant),反應之進行可更具有反應性。不受限於理論,假設氧化催化劑/氧化劑,特別是過氧化物係有助於將烷基鏈氧化成CO2 。氧化催化劑及氧化用劑(oxidating agent)或氧化劑(oxidant)係用於相同化合物。所加入催化劑之催化量(catalytic amount)係低於化學計量;過氧化物若用作氧化用劑(oxidating agent)或氧化劑(oxidant),則係以化學計量之用量加入。氧化用劑(oxidating agent)及氧化劑(oxidant)在本申請案中係同義詞。When the number of carbons in the halocarbon compound is> 1, that is, 2, 3, 4, 5, 6, 7, 8, 9, 10 or higher, the stoichiometric addition of the oxidant seems to be necessary. Here, the oxidant activates the halocarbon compound, which tends to degrade. With the aid of an oxidation catalyst/oxidating agent/oxidant, the progress of the reaction can be more reactive. Without being bound by theory, it is assumed that the oxidation catalyst/oxidant, especially the peroxide system, helps to oxidize the alkyl chain to CO 2 . An oxidation catalyst and an oxidating agent or oxidant are used for the same compound. The catalytic amount of the added catalyst is less than the stoichiometric amount; if peroxide is used as an oxidating agent or oxidant, it is added in a stoichiometric amount. The oxidating agent and oxidant are synonymous in this application.

鹵碳化合物可被加壓至其蒸氣壓,或者若鹵碳化合物在室溫下為液體則以液體型態使用。The halocarbon compound can be pressurized to its vapor pressure, or used in a liquid form if the halocarbon compound is liquid at room temperature.

較佳地,相對於鹵碳化合物的用量,三氧化硫係過量使用。鹵碳化合物與三氧化硫之莫耳比較佳1:100至1:1,更佳1:25至1:1,特別是1:5至1:3。Preferably, sulfur trioxide is used in excess relative to the amount of halocarbon compound. The molar ratio of halocarbon compound and sulfur trioxide is preferably 1:100 to 1:1, more preferably 1:25 to 1:1, especially 1:5 to 1:3.

在較佳實施態樣,鹵碳化合物與三氧化硫之反應係在溫度於0 °C至200 °C之範圍內進行。較佳地,溫度為20 °C至180 °C,尤其是50 °C至160 °C,較佳60 °C至150 °C,更佳80 °C至125 °C,例如100 °C至120 °C。反應溫度越高,反應越快及更有效。但是,溫度太高會產生極度劇烈的情況,因此,需使用在這樣情況下為穩定的反應器。溫度範圍在80 °C及130 °C之間,反應係有效的,且可使用標準配備之任何反應器,因此係經濟的。另外,在較高溫度下,SO2 於H2 SO4 中之溶解度變差。當反應在平衡下,若將產物移除,可改善反應。較高濃度的發煙硫酸,允許較高SO2 耐受度,因此增加產率。基於SO2 在H2 SO4 中之溶劑化作用,SO2 係類似移除的(quasi removed),從而增加反應之有效性(effectivity)。 SO2 及CO2 ,若形成,其之移除可例如使用包括20重量%之NaOH溶液的吸收劑進行。In a preferred embodiment, the reaction of the halocarbon compound and sulfur trioxide is carried out at a temperature in the range of 0 °C to 200 °C. Preferably, the temperature is 20 °C to 180 °C, especially 50 °C to 160 °C, preferably 60 °C to 150 °C, more preferably 80 °C to 125 °C, such as 100 °C to 120 °C. The higher the reaction temperature, the faster and more effective the reaction. However, if the temperature is too high, an extremely severe situation will occur. Therefore, it is necessary to use a reactor that is stable under such conditions. The temperature range is between 80 °C and 130 °C, the reaction is effective, and any standard equipped reactor can be used, so it is economical. In addition, at higher temperatures, the solubility of SO 2 in H 2 SO 4 becomes poor. When the reaction is in equilibrium, if the product is removed, the reaction can be improved. Higher concentrations of oleum allow higher SO 2 tolerance, thus increasing yield. Based on the solvation of SO 2 in H 2 SO 4 , SO 2 is quasi removed, thereby increasing the effectiveness of the reaction. If SO 2 and CO 2 are formed, their removal can be carried out, for example, using an absorbent including a 20% by weight NaOH solution.

在較佳實施態樣,鹵碳化合物與三氧化硫之反應係在壓力1至200巴進行。較佳地,壓力在10至100巴的範圍內,特別是 25至40巴。In a preferred embodiment, the reaction of the halocarbon compound and sulfur trioxide is carried out at a pressure of 1 to 200 bar. Preferably, the pressure is in the range of 10 to 100 bar, especially 25 to 40 bar.

鹵碳化合物可包括任何鹵素。較佳地,鹵碳化合物為烷烴、或烯烴、或炔烴之氟代、氯代及/或溴代衍生物。鹵碳化合物可包括一個或多個鹵素原子。鹵素原子可全部為相同的鹵素元素,即鹵素原子可全部為氟原子、氯原子、或溴原子。或者,鹵碳化合物可包括多於一種類型之鹵素,例如,氟與氯兩者,氟與溴兩者,氯與溴兩者,或氟、氯及溴。The halocarbon compound may include any halogen. Preferably, the halocarbon compound is a fluorinated, chlorinated and/or brominated derivative of alkanes, or alkenes, or alkynes. The halocarbon compound may include one or more halogen atoms. The halogen atoms may all be the same halogen element, that is, all the halogen atoms may be fluorine atoms, chlorine atoms, or bromine atoms. Alternatively, the halocarbon compound may include more than one type of halogen, for example, both fluorine and chlorine, both fluorine and bromine, both chlorine and bromine, or fluorine, chlorine and bromine.

鹵碳化合物包括至少一個鍵結至碳原子的鹵素原子。鹵碳化合物可包括一或多個碳原子鍵結至一或多個鹵素原子。鹵碳化合物一般以Cn H(2n+2)-m Xm 表示。 更簡易的方式,可表示為R-Xm ,其中R為烷基、烯基、芳基,X為F、Cl、或Br,較佳地,X為F。鹵素原子的數目僅限制至可用鍵結的數目,即,若化合物之所有氫原子被取代,X對應於在R基團中氫原子的數目。至少,m=1。The halocarbon compound includes at least one halogen atom bonded to a carbon atom. The halocarbon compound may include one or more carbon atoms bonded to one or more halogen atoms. Halocarbon compounds are generally represented by C n H (2n+2)-m X m . In a simpler way, it can be expressed as RX m , where R is alkyl, alkenyl, or aryl, and X is F, Cl, or Br. Preferably, X is F. The number of halogen atoms is limited only to the number of available bonds, that is, if all hydrogen atoms of the compound are substituted, X corresponds to the number of hydrogen atoms in the R group. At least, m=1.

鹵碳化合物為烷烴、或烯烴、或炔烴之鹵代衍生物。該烷烴、或烯烴、或炔烴較佳為支鏈或無支鏈的烷烴、或烯烴、或炔烴,其中碳數是1至20,尤其是1至15,較佳是1至10,特別是1至5。應理解為上述範圍內之所有數目係同樣被揭示。例如,若碳數是1至20,其表示1或2或3或4或5或6或7或8或9或10或11或12或13或14或15或16或17或18或19或20。較佳範圍亦類似地類推。Halocarbon compounds are halogenated derivatives of alkanes, alkenes, or alkynes. The alkane, or alkene, or alkyne is preferably branched or unbranched alkane, or alkene, or alkyne, wherein the carbon number is 1 to 20, especially 1 to 15, preferably 1 to 10, especially It is 1 to 5. It should be understood that all numbers within the above range are also disclosed. For example, if the carbon number is 1 to 20, it means 1 or 2 or 3 or 4 or 5 or 6 or 7 or 8 or 9 or 10 or 11 or 12 or 13 or 14 or 15 or 16 or 17 or 18 or 19 or 20. The preferred range is similarly deduced.

在較佳實施態樣,該烷烴為甲烷、乙烷、丙烷、丁烷、異戊烷或異丁烷。In a preferred embodiment, the alkane is methane, ethane, propane, butane, isopentane or isobutane.

較佳地,鹵碳化合物為HCF3 、F3 C-CHF=CH2 、林丹(Lindane)、鹵代表面活性劑或鹵代磺酸系表面活性劑、1,1,1,2-四氟乙烷(R134)、PFOAs(全氟辛酸)、CH2 F2 、CH3 F、CF4 、 所有包括F及/或Cl之環境有害冷凍劑、包括F及/或Cl之冷凍劑。Preferably, the halocarbon compound is HCF 3 , F 3 C-CHF=CH 2 , Lindane, halogen representative surfactant or halogenated sulfonic acid surfactant, 1,1,1,2-tetrafluoro Ethane (R134), PFOAs (perfluorooctanoic acid), CH 2 F 2 , CH 3 F, CF 4 , all environmentally hazardous refrigerants including F and/or Cl, and refrigerants including F and/or Cl.

在較佳實施態樣,反應混合物可包括共催化劑M-R,其中M為金屬,較佳係具有氧化態+1至+7之過渡金屬,特別是第一列過渡金屬,且R為-H、-OH、-CH3 、-O-CH3 、-F、-Cl、-Br、-C2 H5 或更高碳數烷、-OC2 H5 或更高碳數氧烷、或適合的無機平衡離子。特別地,諸如CuCl、NiSO4 、CoCl2 、MnCl2 或VCl2 之金屬鹽類係較佳的。In a preferred embodiment, the reaction mixture may include a co-catalyst MR, where M is a metal, preferably a transition metal having an oxidation state of +1 to +7, especially the first row transition metal, and R is -H,- OH, -CH 3 , -O-CH 3 , -F, -Cl, -Br, -C 2 H 5 or higher carbon number alkane, -OC 2 H 5 or higher carbon number oxane, or suitable inorganic Counter ion. In particular, metal salts such as CuCl, NiSO 4 , CoCl 2 , MnCl 2 or VCl 2 are preferable.

在本發明特別佳的實施態樣,鹵碳化合物為氟代烷。在此實施態樣,本發明目的係藉由使氟烷在發煙的硫酸中分解成HSO3 F、CO2 及SO2 而達成。In a particularly preferred embodiment of the present invention, the halocarbon compound is a fluoroalkane. In this embodiment, the object of the present invention is achieved by decomposing halothane into HSO 3 F, CO 2 and SO 2 in fuming sulfuric acid.

在較佳實施態樣,氟烷包括至少一種下式(I)化合物: RFx (I), 其中,R為支鏈或無支鏈烷基,尤其是甲基、乙基、丙基、丁基、異丙基、異丁基、或更高碳數烷基,其中烷基在二級碳或三級碳上的任何位置可任選地經氟原子鹵化。x是氟原子數,氟原子數最大為需要得到飽和氟碳分子之數目。In a preferred embodiment, the halothane includes at least one compound of the following formula (I): RF x (I), wherein R is a branched or unbranched alkyl group, especially methyl, ethyl, propyl, butyl An alkyl group, an isopropyl group, an isobutyl group, or a higher carbon number alkyl group, wherein any position of the alkyl group on the secondary or tertiary carbon can be optionally halogenated with a fluorine atom. x is the number of fluorine atoms, and the maximum number of fluorine atoms is the number of saturated fluorocarbon molecules needed.

氟烷可加壓至其蒸氣壓或者若該氟烷在室溫為液態則以液態形式使用。氟烷分解之反應式如下: Cx Fy + SO3 (發煙硫酸) à HSO3 F + CO2 + SO2 (R1) 其中,x及y為在1至20範圍內之相同或不同的整數。The halothane can be pressurized to its vapor pressure or used in a liquid form if the halothane is liquid at room temperature. The reaction formula of halothane decomposition is as follows: C x F y + SO 3 (oleum) à HSO 3 F + CO 2 + SO 2 (R1) where x and y are the same or different in the range of 1 to 20 Integer.

氟硫酸(HSO3 F)被認為是硫酸無水物與氟化氫之混合物,因此為HF之前驅物。HSO3 F的應用,於其他例子中,係包括作為烷基化、異構化、環加成、 開環聚合及氟磺酸化之催化劑。SO2 可輕易地形成SO3 後回收,及所產生之CO2 所表示之全球暖化潛勢值相較於氟烷並不高(例如,CO2 為1時,CF3 H為14,800)。Fluorosulfuric acid (HSO 3 F) is considered to be a mixture of sulfuric acid anhydride and hydrogen fluoride, so it is a precursor of HF. The application of HSO 3 F, among other examples, includes as a catalyst for alkylation, isomerization, cycloaddition, ring-opening polymerization and fluorosulfonation. SO 2 can be easily formed into SO 3 and then recovered, and the global warming potential value represented by the produced CO 2 is not high compared to halothane (for example, when CO 2 is 1, CF 3 H is 14,800).

藉助於HSO3 F具有寬廣液態範圍(熔點= -89.0o C,沸點= 162.7o C)及SO3 相對低的沸點(沸點= 45o C),可輕易地得到高度濃縮之HSO3 F的硫酸溶液,因而達成HSO3 F之分離。未使用的SO3 可再回收,以用於第二批料。此策略提供將氟烷分解成簡單分子之簡易及更安全的替代方法。氟硫酸(HSO3 F)的形成避免腐蝕性及高毒性HF釋放至反應器,因而可使用用於反應器之傳統材料(例如,不鏽鋼)。With the help of HSO 3 F having a wide liquid range (melting point = -89.0 o C, boiling point = 162.7 o C) and the relatively low boiling point of SO 3 (boiling point = 45 o C), highly concentrated HSO 3 F sulfuric acid can be easily obtained Solution, thus achieving the separation of HSO 3 F. The unused SO 3 can be recycled for use in the second batch. This strategy provides an easy and safer alternative to the decomposition of halothane into simple molecules. The formation of fluorosulfuric acid (HSO 3 F) prevents the corrosive and highly toxic HF from being released into the reactor, so the traditional materials used in the reactor (for example, stainless steel) can be used.

在較佳實施態樣,鹵碳化合物(特別是氟烷)於分解後之產物混合物可透過將SO2 (回收至H2 SO4 )及SO3 蒸餾掉而分離。任選地,FSO3 H可被使用因其在含有發煙的硫酸之混合物中。In a preferred embodiment, the product mixture of halocarbon compounds (especially halothane) after decomposition can be separated by distilling off SO 2 (recovered to H 2 SO 4 ) and SO 3 . Optionally, FSO 3 H can be used because it is in a mixture containing fuming sulfuric acid.

SO2 及CO2 可被NaOH溶液吸收而被分離。SO 2 and CO 2 can be separated by being absorbed by NaOH solution.

伸甲基二(氯硫酸酯)(MBCS ,CH2 (SO3 Cl)2 )、氯甲基氯硫酸酯(CMCS ,ClCH2 (SO3 Cl))可從CH2 Cl2 中之反應混合物中萃取出。將揮發性CH2 Cl2 蒸發,產生純產物。Methylene bis(chlorosulfate) ( MBCS , CH 2 (SO 3 Cl) 2 ), chloromethyl chlorosulfate ( CMCS , ClCH 2 (SO 3 Cl)) can be obtained from the reaction mixture in CH 2 Cl 2 Extracted out. The volatile CH 2 Cl 2 was evaporated to produce pure product.

伸甲基二(鹵硫酸酯)(MBXS,CH2 (SO3 X)2 )、鹵甲基鹵硫酸酯(XMXS ,XCH2 (SO3 X)),其中X=鹵素F、Cl、Br、I,可從適當溶劑中之反應混合物中萃取出,適當溶劑例如CH2 Cl2 、CHCl3 、六氟苯、全氟代溶劑、部分氟代溶劑。Methylene bis(halosulfate) (MBXS, CH 2 (SO 3 X) 2 ), halomethyl halosulfate ( XMXS , XCH 2 (SO 3 X)), where X=halogen F, Cl, Br, I. It can be extracted from the reaction mixture in a suitable solvent, such as CH 2 Cl 2 , CHCl 3 , hexafluorobenzene, perfluorinated solvent, and partially fluorinated solvent.

用於鹵碳化合物,特別是氟烷之回收方法的裝置可包括不鏽鋼反應器,其中鹵碳化合物,特別是氟烷,可以液態或氣態加入,視各試劑之特定蒸氣壓而定。因在此方法中產生HF,且作為HSO3 F被滯留,所以不需要使用特定物質。若鹵碳化合物,特別是氟烷,為氣體,反應器會加壓至適當壓力,此允許在發煙的硫酸中有適當溶解度。The equipment used for the recovery method of halocarbon compounds, especially halothane, may include a stainless steel reactor, wherein halocarbon compounds, especially halothane, can be added in liquid or gaseous state, depending on the specific vapor pressure of each reagent. Since HF is generated in this method and is retained as HSO 3 F, there is no need to use a specific substance. If halocarbons, especially halothanes, are gases, the reactor will be pressurized to an appropriate pressure, which allows proper solubility in the fuming sulfuric acid.

進行鹵碳化合物分解所用裝置可被設置在生產鹵碳化合物,特別是氟烷,之工業製程旁,以避免輸送費用。或者,該裝置可配置於用於產生SO3 整體設備中,及廣泛地用於為現今基礎設施。The equipment used for the decomposition of halocarbon compounds can be installed next to the industrial process for producing halocarbon compounds, especially halothane, to avoid transportation costs. Alternatively, the device can be deployed in the overall equipment for generating SO 3 and widely used as the current infrastructure.

在一替代實施態樣,本發明目的係藉由一種使氟烷在發煙的硫酸中進行分解之方法而達成,該方法包括如下步驟: i)      提供濃度在30%至99%間之發煙的硫酸; ii)     使氟烷,特別是三氟甲烷,與發煙的硫酸在高壓釜或實驗室反應器中進行反應; iii)    將壓力設置為1至200巴; iv)     任選地加入如上所定義作為催化劑之過氧化物或過氧化物鹽類,若鹵碳化合物包括1個碳原子時;若鹵碳化合物之碳原子數>1時,則以化學計量之量加入。 v) 控制反應混合物溫度在0 °C至150 °C,較佳地55至100 °C,更佳地60至70°C; vi)     若需要,藉由蒸餾或萃取純化反應產物。In an alternative embodiment, the object of the present invention is achieved by a method of decomposing halothane in fuming sulfuric acid. The method includes the following steps: i) Provide smoky sulfuric acid with a concentration between 30% and 99%; ii) Let halothane, especially trifluoromethane, react with fuming sulfuric acid in an autoclave or laboratory reactor; iii) Set the pressure to 1 to 200 bar; iv) Optionally add peroxides or peroxide salts as defined above as catalysts, if the halocarbon compound includes 1 carbon atom; if the number of carbon atoms in the halocarbon compound> 1, then the stoichiometric amount The amount is added. v) Control the temperature of the reaction mixture at 0 °C to 150 °C, preferably 55 to 100 °C, more preferably 60 to 70 °C; vi) If necessary, purify the reaction product by distillation or extraction.

實施例Example

實施例 1 :氟仿分解產生氟硫酸

Figure 02_image003
Example 1 : Fluoroform decomposition to produce fluorosulfuric acid
Figure 02_image003

在包含1.789 kg之36%發煙的硫酸的4升不鏽鋼高壓反應器中加入285克氟仿(4.07莫耳)。反應器密封並加熱至100o C,攪拌速度設為350 rpm。固定攪拌24小時後,過量壓力釋放至裝有硫酸之一組洗滌器中,且過量氟仿,若有,則儲存於不鏽鋼圓筒以避免氟仿釋放至大氣中。反應器內壓力保持固定在30.7巴,此表示為液態之溶解的CF3 H存在,及氣態CF3 H存在於上方頂空。將液體樣品輸送至J-Young核磁管,19 F NMR相對於內部標準測量顯示氟硫酸產率20%(基於氟仿之起始莫耳數)。A 4-liter stainless steel high-pressure reactor containing 1.789 kg of 36% fuming sulfuric acid was charged with 285 grams of fluoroform (4.07 moles). The reactor was sealed and heated to 100 o C, and the stirring speed was set to 350 rpm. After 24 hours of constant stirring, the excess pressure was released to a set of scrubbers equipped with sulfuric acid, and the excess fluoroform, if any, was stored in a stainless steel cylinder to prevent the fluoroform from being released into the atmosphere. The pressure in the reactor remains fixed at 30.7 bar, which means the presence of dissolved CF 3 H in liquid and gaseous CF 3 H in the upper headspace. The liquid sample was transferred to a J-Young nuclear magnetic tube, and 19 F NMR relative to the internal standard measurement showed that the yield of fluorosulfuric acid was 20% (based on the initial molar number of fluoroform).

實施例Example 2:2: 氟仿分解產生氟硫酸Fluoroform decomposition produces fluorosulfuric acid

a) 在包含288.2克之34%發煙的硫酸的400毫升不鏽鋼高壓反應器中加入19克氟仿(0.27莫耳),反應器壓力增加至17.3巴。反應器密封並加熱至80o C,攪拌速度設為400 rpm。引發劑係透過將2.65克K2 S2 O8 (9.8毫莫耳)溶於12毫升H2 SO4 (98%)製得,此混合物透過HPLC泵加至反應器。固定攪拌4天後,過量壓力釋放至裝有硫酸之一組洗滌器中,且過量氟仿儲存於不鏽鋼圓筒以避免直接釋放至大氣中。液體樣品輸送至J-Young核磁管,19 F NMR相對於內部標準測量顯示氟硫酸產率57%(基於氟仿之起始莫耳數)。a) In a 400 ml stainless steel high-pressure reactor containing 288.2 g of 34% fuming sulfuric acid, 19 g of fluoroform (0.27 mol) is added, and the reactor pressure is increased to 17.3 bar. The reactor was sealed and heated to 80 o C, and the stirring speed was set to 400 rpm. The initiator was prepared by dissolving 2.65 g of K 2 S 2 O 8 (9.8 millimoles) in 12 ml of H 2 SO 4 (98%), and this mixture was added to the reactor via an HPLC pump. After 4 days of stationary stirring, the excess pressure was released to a set of scrubbers equipped with sulfuric acid, and the excess fluoroform was stored in a stainless steel cylinder to avoid direct release to the atmosphere. The liquid sample was transferred to the J-Young nuclear magnetic tube, and 19 F NMR relative to the internal standard measurement showed that the yield of fluorosulfuric acid was 57% (based on the initial molar number of fluoroform).

b)在不加入額外氧化劑下製備: CHF3 + 3SO3 + H2 SO4 à 3FSO3 H + CO2 +SO2 b) Prepared without adding additional oxidizing agent: CHF 3 + 3SO 3 + H 2 SO 4 à 3FSO 3 H + CO 2 +SO 2

配備有玻璃襯層之小不鏽鋼反應器(450毫升,購自Parr Instruments)於40°C下加入發煙硫酸65(292.5克,2.37莫耳SO3 )。在劇烈攪拌下,密封的容器加熱至100°C且達到壓力4.2巴。之後,反應器用CHF3 加壓至總壓為15.3巴(94毫莫耳CHF3 )。另外攪拌(900 rpm)反應混合物22小時。然後,反應器冷卻至40°C,及所有揮發物被釋放至裝有硫酸之洗滌器。液態反應混合物回收並存放在100毫升玻璃SCHOTT瓶。A small stainless steel reactor (450 ml, purchased from Parr Instruments) equipped with a glass liner was charged with oleum 65 (292.5 g, 2.37 mol SO 3 ) at 40°C. Under vigorous stirring, the sealed container was heated to 100°C and reached a pressure of 4.2 bar. Afterwards, the reactor was pressurized with CHF 3 to a total pressure of 15.3 bar (94 millimoles CHF 3 ). The reaction mixture was stirred (900 rpm) for an additional 22 hours. Then, the reactor was cooled to 40°C, and all volatiles were released to the scrubber containing sulfuric acid. The liquid reaction mixture was recovered and stored in a 100 ml glass SCHOTT bottle.

少量樣品(約0.7毫升)輸送至有鐵氟龍蓋之核磁管,並透過19 F{1 H} NMR光譜儀進行分析。藉由相關譜峰積分值與內部標準(C6 F6 )比較而測量FSO3 H產量(28.2克,282毫莫耳),顯示CHF3 定量轉換成FSO3 H。A small amount of sample (approximately 0.7 ml) is delivered to a nuclear magnet tube with a Teflon cover, and analyzed by a 19 F{ 1 H} NMR spectrometer. The FSO 3 H production (28.2 g, 282 millimoles) was measured by comparing the relevant peak integral value with the internal standard (C 6 F 6 ), showing that CHF 3 was quantitatively converted into FSO 3 H.

實施例 3: 二氟甲烷( CH2 F2 分解

Figure 02_image005
Example 3: Decomposition difluoromethane (CH 2 F 2) of
Figure 02_image005

配備有玻璃襯層之小不鏽鋼反應器(450毫升,購自Parr Instruments)在60°C下用CH2 F2 加壓至總壓為15.1巴(0.243毫莫耳CH2 F2 );反應 1 然後,發煙硫酸35(oleum 35)(307.2克,等於1.23莫耳SO3 )泵送至反應器。溫度保持在50°C,觀察到壓力為19.2巴。攪拌(900 rpm),壓力降至11.5巴。在劇烈攪拌下,密封的容器加熱至60°C。30小時後,壓力降至大氣壓力。自反應器取少量樣品進行19 F NMR圖譜分析,之後,反應器於60°C下用12.8巴CH2 F2 (0.20莫耳)加壓以進行第二次實驗。36小時後,反應器壓力達1.5巴;反應 2 A small stainless steel reactor (450 ml, purchased from Parr Instruments) equipped with a glass liner was pressurized with CH 2 F 2 at 60°C to a total pressure of 15.1 bar (0.243 millimoles CH 2 F 2 ); reaction 1 . Then, oleum 35 (307.2 grams, equal to 1.23 moles of SO 3 ) was pumped to the reactor. The temperature was maintained at 50°C and a pressure of 19.2 bar was observed. With stirring (900 rpm), the pressure is reduced to 11.5 bar. Under vigorous stirring, the sealed container was heated to 60°C. After 30 hours, the pressure dropped to atmospheric pressure. A small amount of samples were taken from the reactor for 19 F NMR spectrum analysis. After that, the reactor was pressurized with 12.8 bar CH 2 F 2 (0.20 mol) at 60°C for the second experiment. After 36 hours, the reactor pressure reached 1.5 bar; reaction 2 .

FSO3 H於反應 1 之產量(45.1克,0.451莫耳,相對於CHF3 產率為93%)係藉由相關譜峰積分值與內部標準(28.8毫克 C6 F6 )比較而測得。19 F{1 H}(40.89 MHz)NMR s 45.7(FSO3 H); s 161.5 ppm(C6 F6 )ppm。The yield of FSO 3 H in reaction 1 (45.1 g, 0.451 mol, 93% relative to CHF 3 yield) was measured by comparing the integrated value of the relevant peak with the internal standard (28.8 mg C 6 F 6 ). 19 F{ 1 H} (40.89 MHz) NMR s 45.7 (FSO 3 H); s 161.5 ppm (C 6 F 6 ) ppm.

反應器冷卻至40°C,及所有揮發物被釋放至裝有硫酸之洗滌器。液態反應混合物回收並存放在100毫升玻璃SCHOTT瓶。少量樣品(約0.7毫升)輸送至有鐵氟龍蓋之核磁管,並透過19 F{1 H} NMR光譜儀進行分析,顯示CH2 F2 轉換成FSO3 H及有機產物伸甲基二硫酸酯(MDS, CH2 (SO4 H)2 )。The reactor was cooled to 40°C, and all volatiles were released to the scrubber containing sulfuric acid. The liquid reaction mixture was recovered and stored in a 100 ml glass SCHOTT bottle. A small amount of sample (approximately 0.7 ml) was transferred to a nuclear magnetic tube with a Teflon cover, and analyzed by a 19 F{ 1 H} NMR spectrometer, which showed that CH 2 F 2 was converted into FSO 3 H and the organic product ethylene disulfate (MDS, CH 2 (SO 4 H) 2 ).

FSO3 H於反應 2 (第二次CHF3 裝料)之產量(28.4克,0.284莫耳,相對於CHF3 產率為70%)係藉由相關譜峰積分值與內部標準(C6 F6 )比較而測得。The yield of FSO 3 H in reaction 2 (the second CHF 3 charge) (28.4 g, 0.284 mol, relative to the yield of CHF 3 is 70%) is based on the relevant peak integral value and internal standard (C 6 F 6 ) Measured by comparison.

實施例 4 二氯甲烷( CH2 Cl2 )在 不使用催化劑下 之有效分解

Figure 02_image007
Example 4 : Effective decomposition of dichloromethane ( CH 2 Cl 2 ) without catalyst
Figure 02_image007

配備有壓力計及磁力攪拌棒之Fisher Porter壓力反應容器裝入發煙硫酸34(Oleum 34)(27,277克)。在不冷卻下,將二氯甲烷(DCM, 3毫升)緩慢地直接加至發煙硫酸。小心,因為當DCM沒有小心地逐滴加入,反應是劇烈的。反應混合物形成兩個相。關閉Fisher Porter容器,混合物在劇烈攪拌下加熱至90°C。3小時後,停止攪拌,讓反應混合物冷卻至室溫。在此時,無相分離。A Fisher Porter pressure reaction vessel equipped with a pressure gauge and a magnetic stirring rod was filled with Oleum 34 (27,277 g). Without cooling, dichloromethane (DCM, 3 mL) was slowly added directly to the fuming sulfuric acid. Be careful, because when DCM is not carefully added dropwise, the reaction is violent. The reaction mixture formed two phases. The Fisher Porter vessel was closed and the mixture was heated to 90°C under vigorous stirring. After 3 hours, the stirring was stopped and the reaction mixture was allowed to cool to room temperature. At this time, there is no phase separation.

之後,少量樣品(約0.7毫升)輸送至有鐵氟龍蓋之核磁管,並透過1 H及13 C{1 H}以及13 C1 H HSQC NMR光譜儀進行分析,顯示CH2 Cl2 全部轉換(s, 5.36 ppm,1 H NMR)及形成主要產物伸甲基二(氯硫酸酯) MBCS(1 H NMR br s, 6.07 ppm,13 C{1 H}, NMR s 91.77 ppm)。After that, a small amount of sample (approximately 0.7 ml) was transferred to a nuclear magnetic tube with a Teflon cap, and analyzed by 1 H and 13 C{ 1 H} and 13 C 1 H HSQC NMR spectrometers, which showed that CH 2 Cl 2 was completely converted ( s, 5.36 ppm, 1 H NMR) and the formation of the main product, methylene bis(chlorosulfate) MBCS ( 1 H NMR br s, 6.07 ppm, 13 C{ 1 H}, NMR s 91.77 ppm).

當存在過量的CH2 Cl2 ,則隨後形成氯甲基氯硫酸酯(CMCS)。When there is excess CH 2 Cl 2 , chloromethyl chlorosulfate (CMCS) is subsequently formed.

如下NMR化學位移(ppm),由Bethell等人報導於Org. Biomol. Chem. 2004, 2, 1554-62。MBCS :13 C: 92.181 H: 6.14,於CDCl3 中;CMCS :13 C: 77.321 H: 5.96,於CDCl3 中。 所發現的NMR化學位移(ppm):MBCS :13 C: 91.771 H: 6.07,於H2 SO4 中;CMCS :13 C: 76.001 H: 5.86,於H2 SO4 中。The following NMR chemical shifts (ppm) are reported by Bethell et al. in Org. Biomol. Chem. 2004, 2, 1554-62. MBCS : 13 C: 92.18 1 H: 6.14 in CDCl 3 ; CMCS : 13 C: 77.32 1 H: 5.96 in CDCl 3 . Found NMR chemical shifts (ppm): MBCS : 13 C: 91.77 1 H: 6.07 in H 2 SO 4 ; CMCS : 13 C: 76.00 1 H: 5.86 in H 2 SO 4 .

單離:MBCS及CMCS可自反應混合物萃取:小心地用水處理反應混合物以使殘餘SO3 驟冷。然後混合物用二氯甲烷(每次萃取約3毫升)萃取三次。有機層經由PTFE針筒過濾器過濾,所有揮發物在大氣壓下蒸發,製得純產物。Isolation: MBCS and CMCS can be extracted from the reaction mixture: the reaction mixture is carefully treated with water to quench the residual SO 3 . The mixture was then extracted three times with dichloromethane (about 3 ml per extraction). The organic layer was filtered through a PTFE syringe filter, and all volatiles were evaporated under atmospheric pressure to obtain a pure product.

實施例 5 :透過 1,1,1,2- 四氟乙烷( R134 )在發煙的硫酸進行熱分解以製備氟磺酸( FSO3 H R134   + 發煙硫酸34 + 過量K2 S2 O8 à   3FSO3 H  + CO2 (90°C,5巴) Example 5 : Preparation of fluorosulfonic acid ( FSO 3 H ) by thermal decomposition of 1,1,1,2- tetrafluoroethane ( R134 ) in fuming sulfuric acid R134 + fuming sulfuric acid 34 + excess K 2 S 2 O 8 à 3FSO 3 H + CO 2 (90°C, 5 bar)

高壓核磁管(NORELL,EXTREME系列等級3,薄壁,Kalrez O形環)裝入0.5毫升發煙硫酸34(Oleum 34),然後用5巴 1,1,1,2-四氟乙烷(R134)加壓。反應後,進行1 H及19 F NMR圖譜分析。 起始物料: R134在發煙硫酸34中之19 F(40.89 MHz) NMR: -75,5(3F, dt, J=15.9;8.1 Hz, CF 3 ); -236.4(1F, tq J=45.5; 15.6, ppm, CH2 F )ppm。 R134在發煙硫酸34中之1 H NMR(44 MHz):4.77(2H, dq, J=45.1; 8.1 Hz, CH 2 F)。The high-pressure nuclear magnetic tube (NORELL, EXTREME series grade 3, thin wall, Kalrez O-ring) is filled with 0.5 ml of oleum 34 (Oleum 34), and then 5 bar 1,1,1,2-tetrafluoroethane (R134 ) Pressure. After the reaction, 1 H and 19 F NMR spectrum analysis was performed. Starting material: 19 F (40.89 MHz) of R134 in oleum 34 NMR: -75,5 (3F, dt, J=15.9; 8.1 Hz, C F 3 ); -236.4 (1F, tq J=45.5 ; 15.6, ppm, CH 2 F ) ppm. 1 H NMR (44 MHz) of R134 in oleum 34: 4.77 (2H, dq, J=45.1; 8.1 Hz, C H 2 F).

在85°C不使用氧化劑下,於16小時後沒有偵測到FSO3 H的形成。加入過量K2 S2 O8 可偵測到FSO3 H的形成,此可由2小時內所得19 F NMR圖譜顯示。在85°C下21小時後,1,1,1,2-四氟乙烷(R134)定量地反應,且觀察到FSO3 H產率為85%。1 H NMR圖譜顯示沒有形成主要的無氟代副產物(例如,伸甲基二(硫酸酯)或類似者)。At 85°C without using an oxidizing agent, no formation of FSO 3 H was detected after 16 hours. Adding excess K 2 S 2 O 8 can detect the formation of FSO 3 H, which can be shown by the 19 F NMR spectrum obtained within 2 hours. After 21 hours at 85°C, 1,1,1,2-tetrafluoroethane (R134) reacted quantitatively, and the FSO 3 H yield was observed to be 85%. The 1 H NMR spectrum shows that no major non-fluorinated by-products (for example, methylene bis(sulfate) or the like) are formed.

實施例 6 :透過 2,3,3,3- 四氟丙烯( R1234yf )在發煙的硫酸進行熱分解以製備氟磺酸( FSO3 H R1234yf +發煙硫酸34 + 過量K2 S2 O8 à  3FSO3 H  + CO2 (90°C,5巴) Example 6 : Preparation of fluorosulfonic acid ( FSO 3 H ) by thermal decomposition of 2,3,3,3- tetrafluoropropene ( R1234yf ) in fuming sulfuric acid R1234yf + oleum 34 + excess K 2 S 2 O 8 à 3FSO 3 H + CO 2 (90°C, 5 bar)

高壓核磁管(NORELL,EXTREME系列等級3,薄壁,Kalrez O形環)裝入0.5毫升發煙硫酸34,然後用5巴2,3,3,3-四氟丙烯(R1234yf)加壓。反應後進行1 H及19 F NMR圖譜分析。R1234yf於發煙硫酸34中之19 F{1 H}(40.89 MHz)NMR:於約-74(br)ppm的寬單峰(br s)疊加光譜儀之固有的殘餘譜峰。The high-pressure nuclear magnet tube (NORELL, EXTREME series grade 3, thin wall, Kalrez O-ring) is filled with 0.5 ml of oleum 34, and then pressurized with 5 bar 2,3,3,3-tetrafluoropropene (R1234yf). After the reaction, 1 H and 19 F NMR spectrum analysis were performed. 19 F{ 1 H} (40.89 MHz) NMR of R1234yf in oleum 34: a broad single peak (br s) of approximately -74 (br) ppm superimposed on the inherent residual peak of the spectrometer.

在周溫不使用氧化劑下,於15分鐘後已偵測到FSO3 H的形成。在90°C於1小時後,19 F NMR圖譜除了包括在44 ppm與FSO3 H相關之單峰外,僅包括另外三個單峰(-70.0; -75.2; -76.4 ppm)。明顯地,不存在J 偶合(J coupling),表示只有C-F部分,但沒有任何偶合的H或F相鄰原子。When no oxidizing agent is used at ambient temperature, the formation of FSO 3 H has been detected after 15 minutes. After 1 hour at 90°C, the 19 F NMR spectrum includes only three single peaks (-70.0; -75.2; -76.4 ppm) in addition to the single peak associated with FSO 3 H at 44 ppm. Obviously, there is no J coupling, which means that there is only the CF part, but there are no coupled H or F adjacent atoms.

釋放壓力並沒有造成與起始形成之副產物相關於單峰共振的耗損,因此預期中間產物並非氣態。至混合物加入過量K2 S2 O8 (200毫克)。加入K2 S2 O8 時,觀察到氣體劇烈形成。反應混合物在關閉之核磁管另於90°C下加熱6小時。觀察到與FSO3 H相關之峰面積的增加。然而,殘峰仍存在-65與- 80ppm之間的面積。Releasing the pressure did not cause the loss of the unimodal resonance associated with the initially formed by-products, so the intermediate product is not expected to be gaseous. To the mixture was added excess K 2 S 2 O 8 (200 mg). When K 2 S 2 O 8 was added, gas formation was observed violently. The reaction mixture was heated at 90°C for another 6 hours in the closed NMR tube. An increase in the peak area associated with FSO 3 H is observed. However, the residual peak still exists in the area between -65 and -80 ppm.

R1234yf 轉換率:100%。 相對於所有形成之含F產物,FSO3 H產率:60%。R1234yf conversion rate: 100%. Relative to all the F-containing products formed, the yield of FSO 3 H: 60%.

實施例 7 :透過全氟辛酸於發煙的硫酸中之熱分解製備氟磺酸( FSO3 H PFOA +發煙硫酸34 + 過量K2 S2 O8 à   3FSO3 H  + CO2 (80°C) Example 7 : Preparation of fluorosulfonic acid ( FSO 3 H ) by thermal decomposition of PFOA in fuming sulfuric acid PFOA + fuming sulfuric acid 34 + excess K 2 S 2 O 8 à 3FSO 3 H + CO 2 (80°C)

J Young 核磁管(NORELL)裝入0.5毫升發煙硫酸34及15毫克全氟辛酸(PFOA)。反應後進行19 F NMR圖譜分析。在沒有氧化劑的情況下,於80°C下歷經3小時沒有反應發生。加入過量K2 S2 O8 並在80°C加熱樣品30分鐘,透過19 F NMR圖譜分析,觀察到FSO3 H的形成。使反應物反應整夜(16小時),PFOA顯著降解及確認FSO3 H的形成。J Young NMR tube (NORELL) is filled with 0.5 ml of oleum 34 and 15 mg of perfluorooctanoic acid (PFOA). After the reaction, 19 F NMR spectrum analysis was performed. In the absence of an oxidant, no reaction occurred after 3 hours at 80°C. Add excess K 2 S 2 O 8 and heat the sample at 80°C for 30 minutes. According to 19 F NMR spectrum analysis, the formation of FSO 3 H is observed. The reactants were allowed to react overnight (16 hours), PFOA was significantly degraded and the formation of FSO 3 H was confirmed.

PFOA轉換率:70%。PFOA conversion rate: 70%.

no

no

無。no.

Claims (16)

一種轉換鹵碳化合物的方法,其中鹵碳化合物與三氧化硫(SO3 )反應。A method of converting halocarbon compounds, in which halocarbon compounds react with sulfur trioxide (SO 3 ). 如請求項1所述的方法,其中SO3 係以發煙硫酸(oleum)存在。The method according to claim 1, wherein SO 3 is present as oleum. 如請求項1或2所述的方法,其中,鹵碳化合物與SO3 反應形成對應的鹵代磺酸(halide sulfonic acid)。The method according to claim 1 or 2, wherein the halide compound reacts with SO 3 to form a corresponding halide sulfonic acid. 如請求項1或2所述的方法,其中,鹵碳化合物為烴中至少一個氫原子被鹵素取代後之化合物,該烴係選自烷烴、烯烴、炔烴(alkine),其中該烴可為直鏈的、支鏈的或環狀的、經取代或未經取代的。The method according to claim 1 or 2, wherein the halocarbon compound is a compound in which at least one hydrogen atom in a hydrocarbon is replaced by a halogen, and the hydrocarbon system is selected from alkanes, alkenes, and alkynes, wherein the hydrocarbon may be Linear, branched or cyclic, substituted or unsubstituted. 如請求項1或2所述的方法,其中,三氧化硫與鹵碳化合物之分子比在1至100的範圍內。The method according to claim 1 or 2, wherein the molecular ratio of sulfur trioxide to halocarbon compound is in the range of 1 to 100. 如請求項1或2所述的方法,其中,鹵碳化合物與SO3 在0至200 °C之溫度下反應。The method according to claim 1 or 2, wherein the halocarbon compound is reacted with SO 3 at a temperature of 0 to 200 °C. 如請求項1或2所述的方法,其中,鹵碳化合物與SO3 在1至200巴之壓力下反應。The method according to claim 1 or 2, wherein the halocarbon compound is reacted with SO 3 under a pressure of 1 to 200 bar. 如請求項1或2所述的方法,其中,鹵碳化合物是烷烴的氟代、溴代或氯代衍生物。The method according to claim 1 or 2, wherein the halocarbon compound is a fluoro, bromo or chloro derivative of alkane. 如請求項1或2所述的方法,其中,鹵碳化合物包括一或多個鹵素原子,其中鹵碳化合物之一或多個碳原子係鍵結至一或多個鹵素原子。The method according to claim 1 or 2, wherein the halocarbon compound includes one or more halogen atoms, wherein one or more carbon atoms of the halocarbon compound are bonded to one or more halogen atoms. 如請求項1或2所述的方法,其中,鹵碳化合物是具有碳數在1至20的範圍內之支鏈或無支鏈的烷烴的鹵代衍生物(halogenated derivative)。The method according to claim 1 or 2, wherein the halogenated carbon compound is a halogenated derivative of a branched or unbranched alkane having a carbon number in the range of 1 to 20. 如請求項1或2所述的方法,其中,將過氧化物加至包括鹵碳化合物及發煙硫酸的反應混合物。The method according to claim 1 or 2, wherein the peroxide is added to the reaction mixture including the halocarbon compound and fuming sulfuric acid. 如請求項11所述的方法,其中,當鹵碳化合物包括多於1個碳原子時,過氧化物以化學計量的用量加入,當鹵碳化合物包括1個碳原子時,過氧化物以低於化學計量的用量(sub-stoichiometrically)加入。The method according to claim 11, wherein when the halocarbon compound includes more than 1 carbon atom, the peroxide is added in a stoichiometric amount, and when the halocarbon compound includes 1 carbon atom, the peroxide Add in stoichiometrically (sub-stoichiometrically). 如請求項1或2所述的方法,其中,在反應期間產生硫酸化中間產物。The method according to claim 1 or 2, wherein a sulfated intermediate product is produced during the reaction. 如請求項13所述的方法,其中,該硫酸化中間產物可自反應混合物分離。The method according to claim 13, wherein the sulfated intermediate product can be separated from the reaction mixture. 一種三氧化硫於鹵碳化合物的回收或處置的用途。A use of sulfur trioxide in the recovery or disposal of halocarbon compounds. 如請求項15所述的用途,其中, 三氧化硫係用於氟烷之回收或處置。The use according to claim 15, wherein the sulfur trioxide is used for the recovery or disposal of halothane.
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